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<br /> <br />260 <br /> <br />atures. No hatching occurred at go C. Our results <br />differ from Marsh (1985) and Toney (1974) who <br />found total egg mortality occurring at 10" C. Marsh <br />(1985) also reported reduced hatching at 150.C. The <br />development rates we observed were less than <br />those reported by Minckley & Gustafson (1982) <br />and Marsh (1985) at corresponding temperatures. <br />This may have resulted from lower initial spawning <br />and preacclimation temperatures of adults and <br />eggs in our study. <br />Our success in incubating eggs at lower temper- <br />atures may reflect simulation of natural conditions <br />to a greater degree than those of previous investi- <br />gators. Marsh (1985) and Toney (1974) had higher <br />acclimation temperature gradients (higher preac- <br />climation temperatures). used formaldehyde to <br />control fungus. and hormonally-induced matuTCI- <br />tion of ova. Eggs used by Marsh (1985) were <br />spawned at 17.5-18"C and those used by Toney <br />(1974) were at 160C before being acclimated to <br />lower temperatures. Different stages of embryonic <br />development are more sensitive to both negative <br />changes and the degree of change in temperature <br />(Alabaster & Uoyd 1980. Cloud et at 19N8). In <br />both studies. embryos were treated with formalde- <br />hyde but the synergistic effects of formaldehyde <br />and reduced temperatures are unknown, to us. <br />Minckler & Gustafson (1982) found that \Wrmon- <br />ally-inducefl ovulation resulted in razorback sucker <br />eggs averaging 1.8 mm diameter. while naturally- <br />ripened eggs averaged 2.9mm. Egg diameters in <br />our experiments using natur-llly-ripened fish <br />(mean = 3.1:t O.4sd) were similar to the latter. <br />It is difficult to control all external variables and <br />look solely at incubation response to temperature <br />differences. Our use of naturally-ripc:ned adults. <br />lower temperature acclimation. and avoidance of <br />formaldehyde may have contributed to differences <br />between our results and those of others. The varia- <br />bility in hatching success among our experiments <br />may indicate the presence of other factors influen- <br />cing hatching success. Auctuations in temperature <br />in the experimental chambers may have increased <br />mortality at HrC. Temperature buffering in thc <br />reservoir may reduce this source of mortality and <br />therefore may not bc as significant in Lake Mo- <br />have. <br /> <br />IlIfluC'l/ce of temperature 011 reproductiol/ <br /> <br />Temperature is an important regulator of metabo- <br />lic and development rates in fish embryos (Win- <br />berg 1956. Hoar & Randall 1969. Colby & Brooke <br />1973). Embryonic dcvelopment is fasler al higher <br />temperatures. but is confined within some physio- <br />logiC-ell minimum and maximum tcmperature that is <br />specifIC to individual species. Optim..l rang~'S of <br />embryonic incubation temperatures of many s~- <br />cies tlf freshW'cder fish can vary. spanning a range of <br />about geC or more (Alaba...tcr & Lloyd l\Jx()). <br />Thc..-se optimal ranges are often concurrent with <br />temperatures selected by that species in nature for <br />spawning. Spawning also often occurs above and <br />below these optimal temper.ltures. However. there <br />is an 1ncreasc in mortalities and abnonmtlitics a...so- <br />dated with incubation in these temperature ranges <br />(Alabaster & Lloyd 19HO). <br />Hatching success. largely influenced by temper- <br />atures during the spawning season. can ultimately <br />affc,-'1 year class strength offL'\h (Serns 1984. Reck- <br />alln 11.)86, Coutant 1987. Kalkmeyn 1987). The <br />wider r.mge of optimal incubation tempcmtures in <br />freshwater fishes relative to marine fishes is be. <br />lieved to bc an adaptation to the more variable <br />thermal regimes occurring in freshwater systems <br />(Alabaster & Lloyd 1980. Cushing 1982). Cushing <br />(1~) further suggests that longer spawning peri- <br />(xis by some spc..'Cies arc a Ilkochanism to reduce <br />year class failure by having at least some larvae <br />emerging during times of optimal environmental <br />conditions. <br /> <br />Razorback sucker-white suda~r spawni"g <br /> <br />Linle is known about the pre-impounded riverine <br />spawning. incubation. and ecology of the relzor- <br />back sucker. particularly in regard to temperature. <br />Reduced temperatures from hypolimnetic dis- <br />charges of dams are implied as a contributing factor <br />to lhe decline in distribution and abund.mce of the <br />species (Johnson & Rinne 19H2. Marsh 1%5). <br />However. the exact mechanism of this inter.lction <br />is unknown. Comparison of incubation and rearing <br />temperatures betwecn the r.lzorback sucker and <br />